Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 239-931-4 | CAS number: 15827-60-8
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2002-03-28 to 2002-04-25
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: Test Method Relating to New Chemical Substances (1974, amended 1998)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 305 (Bioconcentration: Flow-through Fish Test)
- GLP compliance:
- yes
- Details on sampling:
- - Sampling intervals/frequency for test organisms: 4, 7, 14, 21, and 28 days
- Sampling intervals/frequency for test medium samples:0, 4, 7, 14, 21, and 28 days
- Details on sampling and analysis of test organisms and test media samples (e.g. sample preparation, analytical methods):
- Four fish were taken from each concentration level and analysed two by two. Two fish are weighed, cut into pieces, and homogenised to a slurry. 15ml Acetonitrile, 5ml purified water and 0.2 ml of triethylamine were added to 1g of slurry. The solution was homogenised, centrifuged adn the top layer collected and diluted to 50ml and then further diluted 20-fold with purified water. The solution was analysed by HPLC.
- The test media at high concentration was diluted ten-fold with purified water, then analysed by HPLC. The test media at low concentration was directly analysed by HPLC. - Details on preparation of test solutions, spiked fish food or sediment:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Test substance dissolved in 2000ml purified water (High concentration level feed: 40000mg/l, low concentration feed: 4000mg/l). Each of feed solutions was supplied to a mixing glass tube by a metering pump, and diluted to their respective nominal concentrations by mixing with dilutionwater delivered by another type of metering pump, then poured into each test chamber. - Test organisms (species):
- Cyprinus carpio
- Details on test organisms:
- TEST ORGANISM
- Common name: Carp
- Source: Sankyo Suisan Co., 1-1, Ichigayatamachi, Shinjuku-ku, Tokyo, Japan, Lot #: 01-K-1112
- Age at study initiation (mean and range, SD): Less than a year after hatching
- Length at study initiation (lenght definition, mean, range and SD): 8±4 cm
- Weight at study initiation (mean and range, SD): About 5 g
- Health status: Preacclimation: When the lot of fish was received, visual observation was made and abnormal fish were removed. The remaining fish were then reared in anaquariumwithwater flowing through. During the acclimation period, fish were kept without receiving medicine in the aquarium.
- Description of housing/holding area: aquarium
- Feeding during test: 200ml/day
ACCLIMATION
- Acclimation period: ≥2 weeks
- Type and amount of food: Babygold® from Kyorin, The food was given in an amount of 2% of the fish weight.
- Health during acclimation (any mortality observed): Mortality during the 1 week before testing: (5% - Route of exposure:
- aqueous
- Test type:
- flow-through
- Water / sediment media type:
- natural water: freshwater
- Total exposure / uptake duration:
- 28 d
- Test temperature:
- 24±2°C
- pH:
- 6.0-8.5
- Dissolved oxygen:
- 260% of the saturation (25 mg/L at 240C)
- Details on test conditions:
- TEST MEDIUM / WATER PARAMETERS
- Intervals of test medium replacement: feed solutions were renewed after about 8 days.
OTHER TEST CONDITIONS
- Light intensity: About 16 hr/day (Hf fluorescent lamp with wavelengths of 400-700 nm) - Type:
- BCF
- Value:
- < 10 dimensionless
- Calculation basis:
- steady state
- Remarks on result:
- other: Conc.in environment / dose:High concentration level (18.8mg/L)
- Type:
- BCF
- Value:
- < 94 dimensionless
- Calculation basis:
- steady state
- Remarks on result:
- other: Conc.in environment / dose:Low concentration level (2.03mg/l)
- Details on results:
- - Mortality of test organisms: <10%
- Behavioural abnormalities: There was no abnormality in shape of the body or in swimming and feeding behavior during the period of the test. - Validity criteria fulfilled:
- yes
- Conclusions:
- Bioconcentration factors of <10 (Concentration level 18.8mg/l) and <94 (concentration level 2.03 mg/l) were determined in a reliable study conducted according to an appropriate test protocol, and in compliance with GLP.
Reference
Table 1: Concentration of the test substance in the test fish and bioconcentration factor (BCF) - High concentration level
Exposure period |
Fish weight (g) |
Peak Area (mAbs.sec) |
Conc. In final solution (mg/l) |
Conc. In fish body (µg/g) |
Mean conc. In water (mg/l) |
BCF |
|||
Day |
No. |
1 |
2 |
Sample |
std |
||||
4 |
1 |
4.64 |
8.79 |
<1500 |
19910 |
<0.151 |
<166 |
18.8 |
<9 |
4 |
2 |
6.94 |
4.84 |
<1500 |
19910 |
<0.151 |
<166 |
18.8 |
<9 |
7 |
1 |
4.70 |
6.44 |
<1500 |
19834 |
<0.151 |
<167 |
19.0 |
<9 |
7 |
2 |
7.49 |
7.41 |
<1500 |
19834 |
<0.151 |
<167 |
19.0 |
<9 |
14 |
1 |
6.27 |
5.61 |
<1500 |
17767 |
<0.169 |
<186 |
18.9 |
<10 |
14 |
2 |
6.82 |
6.40 |
<1500 |
17767 |
<0.169 |
<186 |
18.9 |
<10 |
21 |
1 |
5.59 |
6.27 |
<1500 |
17767 |
<0.169 |
<186 |
18.7 |
<10 |
21 |
2 |
8.74 |
5.87 |
<1500 |
17767 |
<0.169 |
<186 |
18.7 |
<10 |
28 |
1 |
6.44 |
5.56 |
<1500 |
17767 |
<0.169 |
<186 |
18.8 |
<10 |
28 |
2 |
6.46 |
6.75 |
<1500 |
17767 |
<0.169 |
<186 |
18.8 |
<10 |
Table 2: Concentration of the test substance in the test fish and bioconcentration factor (BCF) - Low concentration level
Exposure period |
Fish weight (g) |
Peak Area (mAbs.sec) |
Conc. In final solution (mg/l) |
Conc. In fish body (µg/g) |
Mean conc. In water (mg/l) |
BCF |
|||
Day |
No. |
1 |
2 |
Sample |
std |
||||
4 |
1 |
9.89 |
4.26 |
<1500 |
19910 |
<0.151 |
<166 |
2.06 |
<81 |
4 |
2 |
8.16 |
5.76 |
<1500 |
19910 |
<0.151 |
<166 |
2.06 |
<81 |
7 |
1 |
10.47 |
5.19 |
<1500 |
19834 |
<0.151 |
<167 |
2.01 |
<83 |
7 |
2 |
9.18 |
6.50 |
<1500 |
19834 |
<0.151 |
<167 |
2.01 |
<83 |
14 |
1 |
10.66 |
4.45 |
<1500 |
17767 |
<0.169 |
<186 |
2.00 |
<93 |
14 |
2 |
6.00 |
6.56 |
<1500 |
17767 |
<0.169 |
<186 |
2.00 |
<93 |
21 |
1 |
4.47 |
7.21 |
<1500 |
17767 |
<0.169 |
<186 |
1.99 |
<94 |
21 |
2 |
5.84 |
6.35 |
<1500 |
17767 |
<0.169 |
<186 |
1.99 |
<94 |
28 |
1 |
7.55 |
5.46 |
<1500 |
17767 |
<0.169 |
<186 |
2.03 |
<92 |
28 |
2 |
6.40 |
5.00 |
<1500 |
17767 |
<0.169 |
<186 |
2.03 |
<92 |
Both the final concentration in water and the concentration in fish body are at approximately the limits of detection of the analytical methods for those media.
Description of key information
A reliable study of bioaccumulation of DTPMP-7Na in carp, indicates a bioconcentration factors in the exposure phase of <10 (Concentration level 18.8 mg/l) and <94 (concentration level 2.03 mg/l).
Key value for chemical safety assessment
- BCF (aquatic species):
- 94 dimensionless
Additional information
This conclusion is based upon a reliable study conducted with DTPMP-7Na according to an appropriate test protocol, and in compliance with GLP.
Discussion of trends in the DTPMP category
On the basis of reliable experimental evidence in fish, DTPMP and its salts are not expected to bioaccumulate. Values for direct structural analogues (ATMP, HEDP) are less than 100. QSARs for bioaccumulation are not validated for phosphonates.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.